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Journal articles on the topic 'Pond ecology – New South Wales'

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Author: Grafiati

Published: 10 December 2022

Last updated: 29 January 2023

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1

Mahony, Michael, Francis Lemckert, Andrew Haywood, and Traecey Brassil. "Correlations between frogs and pond attributes in central New South Wales, Australia: What makes a good pond?" Applied Herpetology 3, no. 1 (2006): 67–81. http://dx.doi.org/10.1163/157075406775247012.

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2

Casanova, Michelle T., Annabel Douglas-Hill, Margaret A. Brock, Monika Muschal, and Michael Bales. "Farm ponds in New South Wales, Australia: relationship between macrophyte and phytoplankton abundances." Marine and Freshwater Research 48, no. 4 (1997): 353. http://dx.doi.org/10.1071/mf96131.

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The physical, chemical and biological characteristics of 65 farm ponds in the Northern Tablelands and Central Western Slopes regions of New South Wales, Australia, were similar to those recorded for Australian ponds in other studies. The strongest single relationship between physico-chemical characteristics and biological characteristics was for high abundance of phytoplankton, low abundance of macrophytes, high turbidity, and high nutrient concentrations in ponds on granitic soil. Variation among the ponds was such that no other relationship was significant. Five groups of ponds were discerned on the basis of their biological and physico-chemical characteristics. One group could be classed as reasonably ‘pristine’, with high water clarity and high abundance of macrophytes; another group presented highly eutrophic, phytoplankton-dominated conditions. Ponds in these two groups can be described as being in ‘alternative stable states’. A third group had been modified with the intention of improving the appearance or utility of the ponds. The last two groups identified in this analysis had no specific parallels in the literature. Abundance of macrophytes was related to good water quality, and encouragement of increased abundance of submerged plants in farm ponds could result in improved water quality.

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3

Semeniuk, M., F. Lemckert, and R. Shine. "Breeding-site selection by cane toads (Bufo marinus) and native frogs in northern New South Wales, Australia." Wildlife Research 34, no. 1 (2007): 59. http://dx.doi.org/10.1071/wr06112.

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Previous research on cane toads (Bufo marinus) has documented non-random selection of breeding sites by this invasive species. In the wet–dry tropics of the Northern Territory, toads selected spawning sites in open areas with gently sloping banks and shallow water. If consistent, such biases may present opportunities for toad control via waterbody manipulation – but first we need to know whether such criteria for spawning-site selection (1) are consistent across other parts of the toad’s extensive Australian range, and (2) differ from those of native anurans breeding at the same waterbodies. We quantified the attributes of potential and actual spawning-sites in north-eastern New South Wales, in temperate-zone habitat where cane toads have been present for many decades; our study area thus differs in many ways from the previously studied tropical site. We compared habitat and water chemistry variables between 23 cane toad breeding sites and 23 nearby unused sites. To examine habitat use at an even finer scale, we conducted nocturnal surveys of microhabitat use by calling male toads and native anurans. Our results revealed that cane toads in this region were highly selective in their choice of breeding sites, and that the criteria they used in this respect were similar to those used by toads in the Northern Territory. Calling male cane toads also used microhabitats non-randomly within each pond, apparently based on similar criteria to those used when selecting among ponds. Toads differed significantly from native anurans in these respects, suggesting that it may be feasible to manipulate waterbody attributes to impact on invasive toads without disrupting reproduction by native anurans.

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4

Haywood, Andrew, Traecey Brassil, and Francis Lemckert. "Effects of a low intensity fire on populations of pond breeding anurans in mid-northern New South Wales, Australia." Applied Herpetology 1, no. 3-4 (2004): 183–95. http://dx.doi.org/10.1163/157075403323012188.

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5

Roberts, J., A. Chick, L. Oswald, and P. Thompson. "Effect of carp, Cyprinus carpio L., an exotic benthivorous fish, on aquatic plants and water quality in experimental ponds." Marine and Freshwater Research 46, no. 8 (1995): 1171. http://dx.doi.org/10.1071/mf9951171.

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The effects of carp, Cyprinus carpio L., on water quality and functioning of aquatic systems were investigated in two experiments in ponds (~90 cm deep) outdoors at Griffith, New South Wales. The experiments represented contrasting conditions of high and low impact, defined by stocking density and food availability, with stocking densities chosen to be above and below 450 kg ha-1, the stocking density suggested as a critical threshold for damage. Under high impact conditions, carp had a significant effect on water quality, habitat structure and pond physical characteristics. Turbidity increased from approximately 7 NTU to 26 and 73 NTU by Day 4, there was a complete loss of two out of five plant species tested (Chara fibrosa and Vallisneria sp.) by Day 6, and surface water temperature in ponds with carp was significantly greater by Day 7. Plant loss was attributed to uprooting rather than herbivory, as sometimes reported. Under low impact conditions the uprooting rate of Vallisneria was reduced to a third. Contrary to the results of previous studies, there was no evidence of increased nutrients or greater algal biomass in ponds with carp, but this may have been because the sediments were relatively low in phosphorus. A crude nutrient budget based on water concentrations and tissue analysis showed substantial growth of carp in 20 days that could be accounted for only by considering either sediments or terrestrial inputs (ponds were not covered) as an important food source.

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6

Donnelly, T. H., P. W. Ford, D. McGregor, and D. Allen. "Anthropogenic changes to a billabong in New South Wales. 1. Lagoon evolution and phosphorus dynamics." Marine and Freshwater Research 50, no. 7 (1999): 689. http://dx.doi.org/10.1071/mf98146.

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Anthropogenic changes detected in the sediment of a shallow (~1.6 m) billabong (Horseshoe Lagoon) are the result of a Sewage Treatment Plant (STP) connection in 1958 and catchment urbanization around 1974. Nutrient-rich water caused the collapse of macrophyte populations, algal blooms became common, and urbanization increased sediment deposition (~1 cm year −1 ). Changes in P retention were investigated by using dated cores, pore-water element profiles, and water quality records. The lagoon is the last of three STP holding ponds. Ponds 1 and 2 were sand-mining pits; they receive no sediment input and have negligible P adsorption. The Fe:P ratios in sediments from three Australian rivers have a common slope and this relationship was used to examine Fe:P ratios in the anoxic bottom sediments of the lagoon. A potential for effluent P adsorption developed in the lagoon through Fe mobilization and enrichment in the upper sediments and a strong clay–Fe–P association. The mean long- term P adsorption in the lagoon (35±18%) was the result of maintaining clay input to an oxic waterbody. Bacterial sulfate reduction is the main process decreasing available Fe for effluent P adsorption. Appropriately designed systems could expect to maintain effluent P adsorption efficiencies of around 70%.

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7

PERKINS, PHILIP D. "A revision of the Australian species of the water beetle genus Hydraena Kugelann (Coleoptera: Hydraenidae)." Zootaxa 1489, no. 1 (May 31, 2007): 1–207. http://dx.doi.org/10.11646/zootaxa.1489.1.1.

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The Australian species of the water beetle genus Hydraena Kugelann, 1794, are revised, based on the study of 7,654 specimens. The 29 previously named species are redescribed, and 56 new species are described. The species are placed in 24 species groups. High resolution digital images of all primary types are presented (online version in color), and geographic distributions are mapped. Male genitalia, representative female terminal abdominal segments and representative spermathecae are illustrated. Australian Hydraena are typically found in sandy/gravelly stream margins, often in association with streamside litter; some species are primarily pond dwelling, a few species are humicolous, and one species may be subterranean. The areas of endemicity and species richness coincide quite closely with the Bassian, Torresian, and Timorian biogeographic subregions. Eleven species are shared between the Bassian and Torresian subregions, and twelve are shared between the Torresian and Timorian subregions. Only one species, H. impercepta Zwick, is known to be found in both Australia and Papua New Guinea. One Australian species, H. ambiflagellata, is also known from New Zealand. New species of Hydraena are: H. affirmata (Queensland, Palmerston National Park, Learmouth Creek), H. ambiosina (Queensland, 7 km NE of Tolga), H. antaria (New South Wales, Bruxner Flora Reserve), H. appetita (New South Wales, 14 km W Delagate), H. arcta (Western Australia, Synnot Creek), H. ascensa (Queensland, Rocky Creek, Kennedy Hwy.), H. athertonica (Queensland, Davies Creek), H. australula (Western Australia, Synnot Creek), H. bidefensa (New South Wales, Bruxner Flora Reserve), H. biimpressa (Queensland, 19.5 km ESE Mareeba), H. capacis (New South Wales, Unumgar State Forest, near Grevillia), H. capetribensis (Queensland, Cape Tribulation area), H. converga (Northern Territory, Roderick Creek, Gregory National Park), H. cubista (Western Australia, Mining Camp, Mitchell Plateau), H. cultrata (New South Wales, Bruxner Flora Reserve), H. cunninghamensis (Queensland, Main Range National Park, Cunningham's Gap, Gap Creek), H. darwini (Northern Territory, Darwin), H. deliquesca (Queensland, 5 km E Wallaman Falls), H. disparamera (Queensland, Cape Hillsborough), H. dorrigoensis (New South Wales, Dorrigo National Park, Rosewood Creek, upstream from Coachwood Falls), H. ferethula (Northern Territory, Cooper Creek, 19 km E by S of Mt. Borradaile), H. finniganensis (Queensland, Gap Creek, 5 km ESE Mt. Finnigan), H. forticollis (Western Australia, 4 km W of King Cascade), H. fundaequalis (Victoria, Simpson Creek, 12 km SW Orbost), H. fundata (Queensland, Hann Tableland, 13 km WNW Mareeba), H. hypipamee (Queensland, Mt. Hypipamee National Park, 14 km SW Malanda), H. inancala (Queensland, Girraween National Park, Bald Rock Creek at "Under-ground Creek"), H. innuda (Western Australia, Mitchell Plateau, 16 mi. N Amax Camp), H. intraangulata (Queensland, Leo Creek Mine, McIlwrath Range, E of Coen), H. invicta (New South Wales, Sydney), H. kakadu (Northern Territory, Kakadu National Park, Gubara), H. larsoni (Queensland, Windsor Tablelands), H. latisoror (Queensland, Lamington National Park, stream at head of Moran's Falls), H. luminicollis (Queensland, Lamington National Park, stream at head of Moran's Falls), H. metzeni (Queensland, 15 km NE Mareeba), H. millerorum (Victoria, Traralgon Creek, 0.2 km N 'Hogg Bridge', 5.0 km NNW Balook), H. miniretia (Queensland, Mt. Hypipamee National Park, 14 km SW Malanda), H. mitchellensis (Western Australia, 4 km SbyW Mining Camp, Mitchell Plateau), H. monteithi (Queensland, Thornton Peak, 11 km NE Daintree), H. parciplumea (Northern Territory, McArthur River, 80 km SW of Borroloola), H. porchi (Victoria, Kangaroo Creek on Springhill Rd., 5.8 km E Glenlyon), H. pugillista (Queensland, 7 km N Mt. Spurgeon), H. queenslandica (Queensland, Laceys Creek, 10 km SE El Arish), H. reticuloides (Queensland, 3 km ENE of Mt. Tozer), H. reticulositis (Western Australia, Mining Camp, Mitchell Plateau), H. revelovela (Northern Territory, Kakadu National Park, GungurulLookout), H. spinissima (Queensland, Main Range National Park, Cunningham's Gap, Gap Creek), H. storeyi (Queensland, Cow Bay, N of Daintree River), H. tenuisella (Queensland, 3 km W of Batavia Downs), H. tenuisoror (Australian Capital Territory, Wombat Creek, 6 km NE of Piccadilly Circus), H. textila (Queensland, Laceys Creek, 10 km SE El Arish), H. tridisca (Queensland, Mt. Hemmant), H. triloba (Queensland, Mulgrave River, Goldsborough Road Crossing), H. wattsi (Northern Territory, Holmes Jungle, 11 km NE by E of Darwin), H. weiri (Western Australia, 14 km SbyE Kalumburu Mission), H. zwicki (Queensland, Clacherty Road, via Julatten).

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8

Chessman, BC. "Habitat Preferences of Fresh-Water Turtles in the Murray Valley, Victoria and New-South-Wales." Wildlife Research 15, no. 5 (1988): 485. http://dx.doi.org/10.1071/wr9880485.

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Preferences of Chelodina expansa, Chelodina longicollis and Emydura macquarii (Testudines : Chelidae) for different types of aquatic habitat on the Murray River flood plain in south-eastern Australia were inferred from catch statistics. E. macquarii was the species most often caught in the river itself and river backwaters, whereas C. longicollis formed the majority of captures from oxbow lakes, anabranches, ponds, rain pools and a swamp. Relative abundance of E. macquarii was significantly positively correlated with water body depth, transparency, persistence during dry conditions and flow speed, and negatively correlated with remoteness from the river. C. longicollis demonstrated the opposite pattern, and the proportional catch of C. expansa was weakly correlated with environmental variables. The capacity of C. longicollis for colonising and surviving in small, remote and ephemeral ponds and pools relates to its ability to aestivate and resist desiccation and its propensity for overland migration.

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9

Doubrovsky, A., JL Paynter, SK Sambhi, JG Atherton, and RJG Lester. "Observations on the Ultrastracture of Baculovirus in Australian Penaeus monodon and Penaeus merguiensis." Marine and Freshwater Research 39, no. 6 (1988): 743. http://dx.doi.org/10.1071/mf9880743.

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Baculovirus particles were found in the digestive gland of Penaeus monodon from hatcheries and grow-out ponds in northern New South Wales, northern Queensland and the Northern Territory. Similar particles were seen in a Penaeus merguiensis specimen caught off Townsville, Queensland. The particles were found in the hypertrophied nuclei of hepatopancreatic epithelial cells, both free in the nucleoplasm and occluded in large eosinophilic intranuclear inclusion bodies. The nucleocapsids of the particles measured 45-52 nm × 260-300 nm and resembled the baculovirus reported from Penaeus plebejus.

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10

Schmid, Rudolf, and Gwen J. Harden. "Flora of New South Wales." Taxon 41, no. 3 (August 1992): 627. http://dx.doi.org/10.2307/1222862.

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11

Michael, Damian R., David B. Lindenmayer, Mason Crane, Christopher MacGregor, Rebecca Montague-Drake, and Lachlan McBurney. "Reptilia, Murray catchment, New South Wales, south-eastern Australia." Check List 7, no. 1 (January 1, 2011): 025. http://dx.doi.org/10.15560/7.1.25.

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Two large-scale, long-term biodiversity monitoring programs examining vertebrate responses to habitat fragmentation and landscape change in agricultural landscapes are taking place in the Murray Catchment Management Area of New South Wales, south-eastern Australia. Field surveys involve counting reptiles under a range of management conditions and across a broad range of vegetation types in two bioregions, the South-western Slopes of New South Wales and the Riverina. We list reptiles recorded during surveys conducted between 2002 and 2009. We include additional species recorded between 1997 and 2009 from a conservation reserve. Thirty-nine species from nine families were recorded. The list will be useful for workers interested in reptile zoogeographical distributions and habitat associations as well as those interested in the biodiversity value of remnant vegetation and tree plantings in fragmented agricultural landscapes.

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12

Green, DR. "Rangeland restoration projects in western New South Wales." Rangeland Journal 11, no. 2 (1989): 110. http://dx.doi.org/10.1071/rj9890110.

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The semi-arid to arid Western Division of New South Wales has suffered significant levels of land degradation due to overstocking by domestic animals and rabbits. Three major forms of land degradation are identified, soil erosion, woody weed growth and pasture quality decline. Restoration techniques developed and applied by the New South Wales Soil Conservation Service are presented and discussed. The successful techniques presented are contour furrowing and waterponding for sheet eroded or scalded areas, fire and blade ploughing for woody weed control and grazing management to reverse pasture decline. The lack of knowledge on pasture species responses to grazing management stimuli is highlighted.

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13

Lemckert, Francis Laurence. "Managing pond-breeding anurans in the selectively harvested forests of coastal New South Wales, Australia." Forest Ecology and Management 262, no. 7 (October 2011): 1199–204. http://dx.doi.org/10.1016/j.foreco.2011.06.014.

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14

Schmid, Rudolf, and Gwen J. Harden. "Flora of New South Wales. Vol. 3." Taxon 43, no. 2 (May 1994): 336. http://dx.doi.org/10.2307/1222906.

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15

Rickards, R. B., G. H. Packham, A. J. Wright, and P. L. Williamson. "New name for Silurian graptolite from New South Wales." Alcheringa: An Australasian Journal of Palaeontology 27, no. 1 (January 2003): 77. http://dx.doi.org/10.1080/03115510308619547.

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16

Webby, B. D., and J. Trotter. "A new Ordovician alga from central New South Wales." Alcheringa: An Australasian Journal of Palaeontology 16, no. 1 (January 1992): 87–91. http://dx.doi.org/10.1080/03115519208619033.

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17

Brand, David G. "Forest management in New South Wales, Australia." Forestry Chronicle 73, no. 5 (October 1, 1997): 578–85. http://dx.doi.org/10.5558/tfc73578-5.

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Forest management policy in New South Wales, Australia, has been dramatically changing during the past two decades in response to public controversy and widening expectations of the values that the forest should provide to society. The nature of NSW forest management today is a reflection of the unique Australian forest ecology, the nature of the forest sector, and the emergence of conflict and polarized views on forest management in the past two decades. Recent efforts have made progress in resolving the forest debate. The key elements have included an expanded protected areas reserve system, expanded reliance on plantation forests for wood supply, increased wood security for native forest industries in return for a commitment to value-adding and the implementation of an ecologically sustainable forest management framework. Like other Australian States, NSW is currently negotiating Regional Forest Agreements with the Commonwealth Government that will set the stage for future directions in forest management. Key words: forest policy, Australia, New South Wales forest management

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18

Strusz, Desmond L. "Silurian atrypide brachiopods from Yass, New South Wales." Alcheringa: An Australasian Journal of Palaeontology 31, no. 4 (December 2007): 299–337. http://dx.doi.org/10.1080/03115510701516571.

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19

Webby, B. D., and J. Keith Rigby. "Ordovician sphinctozoan sponges from central New South Wales." Alcheringa: An Australasian Journal of Palaeontology 9, no. 3 (January 1985): 209–20. http://dx.doi.org/10.1080/03115518508618968.

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20

Owen, J. A. K. "Miocene palynomorph assemblages from Kiandra, New South Wales." Alcheringa: An Australasian Journal of Palaeontology 12, no. 4 (January 1988): 269–97. http://dx.doi.org/10.1080/03115518808619128.

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21

Hoare, Richard D., and John R. Farrell. "Lower Devonian Polyplacophora from New South Wales, Australia." Palaeontology 47, no. 6 (November 2004): 1495–506. http://dx.doi.org/10.1111/j.0031-0239.2004.00415.x.

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22

M. Date, E., H. F. Recher, H. A. Ford, and D. A. Stewart. "The conservation and ecology of rainforest pigeons in northeastern New South Wales." Pacific Conservation Biology 2, no. 3 (1995): 299. http://dx.doi.org/10.1071/pc960299.

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A survey of conservation reserves, rainforest remnants and agricultural districts in northeastern New South Wales was conducted to determine the abundance, movements and habitat requirements of rainforest pigeons, to evaluate the extent and use of suitable habitat in conservation reserves, and to provide guidelines for the conservation and management of rainforest pigeons. Eight species of rainforest pigeon occur in northeastern New South Wales. Commencing with the clearing of rainforest in the 1860s for agriculture, rainforest pigeons declined in abundance throughout New South Wales and by the 1970s five species were thought to be threatened in the state. Since then, rainforest pigeons have apparently increased in abundance and distribution, but the Wompoo, Rose-crowned and Superb Pigeons continue to be listed by the New South Wales National Parks and Wildlife Service as vulnerable and rare. However, populations of all species of rainforest pigeons in New South Wales are relatively small and vulnerable to further loss of habitat. Most rainforest pigeons show a preference for subtropical rainforest habitat, but moist eucalypt forests, gardens and weedy exotic vegetation along roads and on abandoned farmland are also frequented to varying degrees by different species. To investigate recent trends in pigeon abundance we used data collected for up to 12 years from eight sites and during 1988, 1989 and 1990 from 17 rainforest remnants in northeastern New South Wales. The data suggest that rainforest pigeons now occur more frequently in lowland agricultural areas than in the recent past and tend to confirm an increase in abundance since the 1970s. Nesting and foraging habitats for rainforest pigeons are extensive in the conservation reserve system of northeastern New South Wales, but these habitats, which are largely at high elevations, lack winter food resources. Instead, pigeons congregate in remnant rainforest and exotic berry-bearing trees and shrubs in agricultural areas at lower elevations and near the coast. They rely on these habitats for food during winter and it is the restricted extent of this habitat that probably limits their abundance, not the area or quality of habitat at higher elevations. The conservation and management of rainforest pigeons requires the protection of low elevation and coastal rainforest remnants. As development of northeastern New South Wales proceeds, to avoid a decline in the abundances of rainforest pigeons it will be necessary to protect sclerophyll forest with native or exotic fruit bearing trees and shrubs and to extend the area of suitable habitat by the regeneration of rainforest and by the planting of native species used by pigeons as a food source. This will become increasingly important as the control and removal of exotic plants, such as Lantana Lantana camara and Camphor Laurel Cinnamonum camphora, on which some pigeons depend as a winter food source, becomes more successful.

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23

Canfield, Paul J. "A SURVEY OF KOALA ROAD KILLS IN NEW SOUTH WALES." Journal of Wildlife Diseases 27, no. 4 (October 1991): 657–60. http://dx.doi.org/10.7589/0090-3558-27.4.657.

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24

Mason, R. J., P. J. S. Fleming, L. D. Smythe, M. F. Dohnt, M. A. Norris, and M. L. Symonds. "LEPTOSPIRA INTERROGANS ANTIBODIES IN FERAL PIGS FROM NEW SOUTH WALES." Journal of Wildlife Diseases 34, no. 4 (October 1998): 738–43. http://dx.doi.org/10.7589/0090-3558-34.4.738.

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25

Witter, D. C. "Regional variation of the archaeology in western New South Wales." Rangeland Journal 26, no. 2 (2004): 129. http://dx.doi.org/10.1071/rj04009.

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There is considerable variation in the Aboriginal archaeology of western New South Wales. This is demonstrated by differences in the stone artefacts found on the open campsites that are common and distributed over all landscapes throughout western NSW. Other site types may occur in particular regions and show differences from one region to another. Eight archaeological regions are proposed. These are at the same scale as the Interim Biogeographic Regionalisation for Australia, and many of the boundaries are the same. The archaeological regions represent the accumulation of archaeological materials on the landscape and Aboriginal knowledge about how to cope in various situations. There is little relationship between the archaeological regional boundaries and the published tribal boundaries. The condition and preservation of the archaeology is closely related to the nature of landscape change since European arrival.

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26

Parry-Jones, K. "Pteropus poliocephalus (Chiroptera: Pteropodidae) in New South Wales." Australian Mammalogy 10, no. 2 (June 1, 1987): 81–85. http://dx.doi.org/10.1071/am87016.

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27

McCarthy, P. M., G. Kantvilas, and J. A. Elix. "Amphorothecium, a new pyrenocarpous lichen genus from New South Wales, Australia." Lichenologist 33, no. 4 (July 2001): 291–96. http://dx.doi.org/10.1006/lich.2001.0330.

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AbstractAmphorothecium occultum P. M. McCarthy, Kantvilas & Elix gen. et sp. nov. is described from deeply shaded, saxicolous bryophytes in south-eastern New South Wales, Australia. This genus is characterized by a trentepohlioid photobiont, distinctive thallus chemistry, pale, simple perithecia, largely unbranched paraphyses and periphyses, thin-walled, non-amyloid asci and very large, multiseptate ascospores. Its systematic position is uncertain.

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28

Grant, T. R., P. C. Gehrke, J. H. Harris, and S. Hartley. "Distribution of the Platypus (Ornithorhynchus anatinus) in New South Wales: Results of The 1994-96 New South Wales Rivers Survey." Australian Mammalogy 21, no. 2 (1999): 177. http://dx.doi.org/10.1071/am00177.

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Data from the New South Wales Rivers Survey on the occurrence of platypuses have provided the most recent and comprehensive record of platypus distribution in the State. The species was most commonly reported from the montane and coastal regions, being less common on the western slopes and uncommon in the rivers of the western lowlands. The observations confirmed those from earlier community-based surveys. In contrast to the distribution of native fish species, there appears to have been little change in the overall state-wide distribution of the platypus in response to degrading processes in the rivers of New South Wales, although nothing is known of the stability of their population numbers.

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29

THEISCHINGER, GUNTHER, and JULIA H. MYNOTT. "A new species of Dinotoperla Tillyard, 1921 from the Shoalhaven Catchment, New South Wales, Australia (Plecoptera: Gripopterygidae)." Zootaxa 4550, no. 3 (January 25, 2019): 423. http://dx.doi.org/10.11646/zootaxa.4550.3.9.

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Dinotoperla cherylae sp. nov. (Holotype ♂: New South Wales, Upper Kangaroo River, 34.672998oS/150.601391oE, 14-Dec-2017) is described from the Shoalhaven Catchment in New South Wales, Australia. The affinities and phylogenetic relationships of the new species are discussed.

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30

Jones, B. G., B. E. Chenhall, A. J. Wright, J. W. Pemberton, and C. Campbell. "Silurian evaporitic strata from New South Wales, Australia." Palaeogeography, Palaeoclimatology, Palaeoecology 59 (January 1987): 215–25. http://dx.doi.org/10.1016/0031-0182(87)90081-2.

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31

Parer, I., and T. Korn. "Seasonal Incidence of Myxomatosis in New-South-Wales." Wildlife Research 16, no. 5 (1989): 563. http://dx.doi.org/10.1071/wr9890563.

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We analysed monthly records of the presence or absence of myxomatosis in the 59 Pasture Protection Board Districts of New South Wales for 1959-64 and 1980-86. These periods respectively precede and follow the introduction of the European rabbit flea, Spilopsyllus cuniculi (Dale), into New South Wales. Throughout New South Wales during the two periods, myxomatosis was reported more frequently in summer than in winter. The seasonal trend was more pronounced on the western and central plains than on the slopes, tablelands or coastal regions. The incidence of myxomatosis was positively related to rainfall on the western and central plains and slopes, but not on the tablelands and coast. After the introduction of the rabbit flea, the reported incidence of myxomatosis increased more on the tablelands than in the other regions.

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32

Kerin, John. "The 1999 review of the Western Division of New South Wales." Rangeland Journal 23, no. 1 (2001): 33. http://dx.doi.org/10.1071/rj01013.

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A comprehensive review of the Western Division of New South Wales was carried out in 1998/99. The review addressed economic, environmental and social issues in New South Wales' rangelands. Six commissioned studies examined these issues in more detail. The recommendations of the review centred on streamlining administrative procedures, including Acts and regulations, addressing integrated natural resource management from a regional perspective by involving leaseholders and relevant stakeholders as representative of the broader community. It was seen as essential that scientific research and expertise, and technological advances in knowledge, be utilised by decision makers in coming to more coordinated land management decisions.

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33

Pickard, John. "Land management in semi-arid environments of New South Wales." Vegetatio 91, no. 1-2 (January 1991): 191–208. http://dx.doi.org/10.1007/bf00036057.

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34

Groves, R. H., J. J. Burdon, and P. E. Kaye. "Demography and Genetics of Onopordum in Southern New South Wales." Journal of Ecology 78, no. 1 (March 1990): 47. http://dx.doi.org/10.2307/2261035.

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35

Pickett, John, and Terry Furey-Greig. "Webbygnathus, a new Late Ordovician conodont genus from New South Wales." Alcheringa: An Australasian Journal of Palaeontology 24, no. 3 (January 2000): 147–52. http://dx.doi.org/10.1080/03115510008619206.

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36

Jeffery, Carolyn J. "Reproductive ecology of the intertidal honeycomb barnacle in New South Wales." Journal of Experimental Marine Biology and Ecology 486 (January 2017): 13–21. http://dx.doi.org/10.1016/j.jembe.2016.09.013.

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37

Graham, Owen P. "Survey of land degradation in New South Wales, Australia." Environmental Management 16, no. 2 (March 1992): 205–23. http://dx.doi.org/10.1007/bf02393826.

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38

Strusz, Desmond L. "Late Silurian strophomenate brachiopods from Yass, New South Wales." Alcheringa: An Australasian Journal of Palaeontology 27, no. 1 (January 2003): 1–35. http://dx.doi.org/10.1080/03115510308619542.

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39

Smith, Elizabeth T. "Early Cretaceous chelids from Lightning Ridge, New South Wales." Alcheringa: An Australasian Journal of Palaeontology 34, no. 3 (September 2010): 375–84. http://dx.doi.org/10.1080/03115518.2010.488117.

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40

Stait, Bryan, Barry D. Webby, and Ian G. Percival. "Late Ordovician nautiloids from central New South Wales, Australia." Alcheringa: An Australasian Journal of Palaeontology 9, no. 2 (January 1985): 143–57. http://dx.doi.org/10.1080/03115518508618962.

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41

Chatterton, Brian D. E., and Anthony J. Wright. "Silicified Early Devonian trilobites from Mudgee, New South Wales." Alcheringa: An Australasian Journal of Palaeontology 10, no. 3 (January 1986): 279–96. http://dx.doi.org/10.1080/03115518608619159.

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42

Timms, B. V. "Study of coastal freshwater lakes in southern New South Wales." Marine and Freshwater Research 48, no. 3 (1997): 249. http://dx.doi.org/10.1071/mf96049.

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There are few freshwater lakes associated with coastal dunes in southern New South Wales (NSW). Lake Nargal near Narooma, Bondi Lake near Bega, and a small lagoon near Pambula have little in common limnologically with coastal dune lakes of northern NSW and southern Queensland. They differ in mode of origin, are less dominated by NaCl, are less acidic, are more speciose, have few characteristic dune-lake indicator species, and moreover contain certain southern species. However, a re-examination of data for Lakes Windermere and McKenzie further north at Jervis Bay suggest that these are classic dune-contact lakes rather similar to those in northern NSW. Differences and similarities are largely influenced by the extent and therefore the hydrological influence of the contextural coastal sand mass and by biogeography.

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43

Apte, Simon C., Graeme E. Batley, Ronald Szymczak, Paul S. Rendell, Randall Lee, and T. David Waite. "Baseline trace metal concentrations in New South Wales coastal waters." Marine and Freshwater Research 49, no. 3 (1998): 203. http://dx.doi.org/10.1071/mf96121.

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Concentrations of ten trace elements at five localities in New South Wales coastal waters were measured by ultratrace sampling and analysis. Mean concentrations of cadmium (2.4 ng L-1), copper (31 ng L-1), nickel (180 ng L-1), lead (9 ng L-1) and zinc (<22 ng L-1) are among the lowest reported in the Southern Hemisphere and are consistent with recent oceanographic data for the surface waters of the Pacific Ocean. Waters from the southernmost sampling locality (Eden) contained higher phosphate, silicate, cadmium and nickel, but lower chromium concentrations than waters from the other four localities, reflecting the inputs of water from the Tasman Sea in the south compared with the dominance of waters from the Coral Sea along the rest of the coast. Cadmium concentrations were positively correlated with both phosphate and silicate. Chromium and lead concentrations were also significantly correlated. It is likely that a major source of lead is atmospheric deposition. The trace metal concentrations were comparable to those in the surface waters of the Pacific Ocean, indicating that fluvial inputs or processes occurring in the coastal margin were of limited importance in determining trace metal concentrations.

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44

Dodson, JR. "Holocene Vegetation and Environments Near Goulburn, New South Wales." Australian Journal of Botany 34, no. 3 (1986): 231. http://dx.doi.org/10.1071/bt9860231.

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Three sites from Breadalbane Basin and one from Wet Lagoon near Goulburn were studied to provide a history of vegetation, fire and lake levels in the region. Stratigraphy, a percentage pollen diagram from each site, an influx diagram from two sites and 29 radiocarbon analyses provided the basic data and chronology of the study. The sedimentary history shows that Breadalbane Basin has undergone several cycles of lake phases with sediment accumulation and dry phases with deflation of the lake sediments. The present lake clays and silts of Breadalbane Basin and Wet Lagoon are all Holocene in age. A lake began forming in Breadalbane Basin before 9300 B.P. and probably reached its greatest extent between 7400 and 2700 B.P. At Wet Lagoon water stands were in evidence from 5000 B.P. Over the last 2000 years the sites have dried out and are ephemeral swamps but their water level histories are not necessarily synchronous. A comparison of the records shows that the vegetation of the region has been open eucalypt woodland with understorey dominated by grasses and herbaceous taxa. The most dramatic change was woodland clearance after the arrival of European settlers. The spread of pollen and charcoal collection sites, however, emphasizes a number of local differences in the vegetation of the region. Casuarina, for example, expanded during the mid Holocene along the escarpment on the western side of Breadalbane Basin. The charcoal input curves show fire was a frequent occurrence in the region but the vegetation was apparently resilient to its effects until European settlers used it as a tool in woodland clearance.

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45

Choi, D., and JA Simpson. "Needle Cast of Pinus radiata in New South Wales." Australian Journal of Botany 39, no. 2 (1991): 137. http://dx.doi.org/10.1071/bt9910137.

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Green needles of 7-9-year-old Pinus radiata trees at a plantation in Sunny Corner, New South Wales, have been infected primarily by two species of fungi, Cyclaneusma minus and Lophodermium pinastri. Needles emerged from fascicle sheaths in October and November and persisted on the trees for about 2 years before developing symptoms of Cyclaneusma minus infection during summer and autumn. Immature current year's needles were infected by both C. minus and L. pinastri before they were fully elongated. Ascospores of C. minus were released from cast needles in very large numbers in spring (September-November) and most new infections occurred during this period. Infection by L. pinastri lagged behind that by C. minus by about 2 months. There was significant between-tree variation in disease levels of each of these fungi. Susceptibility to C. minus was not linked with susceptibility to L. pinastri. Nitrogen levels in P. radiata foliage and symptom expression are correlated.

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46

Millar, AJK, and GT Kraft. "Catalogue of marine benthic green algae (Chlorophyta) of New South Wales, including Lord Howe Island, south-western Pacific." Australian Systematic Botany 7, no. 5 (1994): 419. http://dx.doi.org/10.1071/sb9940419.

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The marine benthic green macroalgae of the New South Wales mainland and of Lord Howe Island are listed, each with bibliographic, distributional and specimen-voucher details. Included are 113 species in 9 orders, 14 families and 38 genera, of which 12 species are based on New South Wales types. With respect to biodiversity, New South Wales is as rich in numbers of genera and species as southern Australia. Eight genera (Pedobesia, Boodlea, Neomeris, Trichosolen, Ventvicaria, Caulerpella, Pseudochlorodesmis, Sporocladopsis) and 41 species are new records for the State, and 14 species are newly recorded for the Australian continent. The largest genus represented is Cladophora; 22 species are recorded, 13 from Lord Howe Island alone, and 7 are new to Australia (C. cymopoliae, C. colabense, C. dotyana, C. nigrescens, C. ohkuboana, C. patentirainea, C. ryukyuensis). Examination of type and recently collected material of Caulerpa annulata (from Port Arthur, Tasmania) shows it to be synonymous with the earlier Caulerpa hodgkinsoniae (from Ballina, New South Wales).

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ADAM, P., P. STRICKER, B. M. WIECEK, and D. J. ANDERSON. "The vegetation of seacliffs and headlands in New South Wales, Australia." Austral Ecology 14, no. 4 (December 1989): 515–45. http://dx.doi.org/10.1111/j.1442-9993.1989.tb01459.x.

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48

Fleming, PJS, and TJ Korn. "Predation of livestock by wild dogs in eastern New South Wales." Rangeland Journal 11, no. 2 (1989): 61. http://dx.doi.org/10.1071/rj9890061.

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A monthly survey involving officers from eastern New South Wales Pastures Protection Boards was conducted over four years from 1982 to 1985. Information was collected on the number and type of livestock attacked within each board district, sightings of wild dogs, the number of wild dogs kiied, the method by which they were kiied and the locations at which the observations occurred. A total of 25,644 livestock animals were reported killed or wounded from four regions; the North-East Coastal Region, the North-East Tablelands Region, the Central-East Region and South-East Region. Sheep were the most commonly attacked domestic animals followed by cattle and goats. Regional differences were apparent in the type of livestock killed and seasonal patterns of predation were evident. We recommend that annual control programmes be brought forward from June/July to late April in order to precede predation peaks.

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49

Hacking, Nicole. "Macrofaunal community structure of beaches in northern New South Wales, Australia." Marine and Freshwater Research 49, no. 1 (1998): 47. http://dx.doi.org/10.1071/mf96130.

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Macrofaunal community composition of ten exposed sandy beaches in northern New South Wales, Australia, appeared to correlate with beach morphodynamic state even though the data represented sampling at only a single time. Better results were obtained by using the Beach State Index (BSI) rather than the dimensionless fall velocity (?). Species number and abundance significantly increased as the BSI value increased, whereas biomass was not correlated with BSI. The New South Wales beaches had a higher species number and abundance relative to BSI than did beaches in a published review of beaches around the world.

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50

Camacho, A. I., and P. Hancock. "A new genus of Parabathynellidae (Crustacea: Bathynellacea) in New South Wales, Australia." Journal of Natural History 44, no. 17-18 (March 31, 2010): 1081–94. http://dx.doi.org/10.1080/00222931003624796.

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